EP3928031A1 - Procédé et réacteur pour le traitement de conversion chimique thermique avancé de déchets solides municipaux - Google Patents

Procédé et réacteur pour le traitement de conversion chimique thermique avancé de déchets solides municipaux

Info

Publication number
EP3928031A1
EP3928031A1 EP20759916.8A EP20759916A EP3928031A1 EP 3928031 A1 EP3928031 A1 EP 3928031A1 EP 20759916 A EP20759916 A EP 20759916A EP 3928031 A1 EP3928031 A1 EP 3928031A1
Authority
EP
European Patent Office
Prior art keywords
canister
waste material
solid waste
waste
reactor
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
EP20759916.8A
Other languages
German (de)
English (en)
Other versions
EP3928031B1 (fr
EP3928031A4 (fr
Inventor
Earl DECKER
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Individual
Original Assignee
Individual
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Filing date
Publication date
Application filed by Individual filed Critical Individual
Publication of EP3928031A1 publication Critical patent/EP3928031A1/fr
Publication of EP3928031A4 publication Critical patent/EP3928031A4/fr
Application granted granted Critical
Publication of EP3928031B1 publication Critical patent/EP3928031B1/fr
Active legal-status Critical Current
Anticipated expiration legal-status Critical

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Classifications

    • C—CHEMISTRY; METALLURGY
    • C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
    • C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
    • C10J3/72—Other features
    • C10J3/726—Start-up
    • C—CHEMISTRY; METALLURGY
    • C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
    • C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
    • C10J3/72—Other features
    • C10J3/78—High-pressure apparatus
    • C—CHEMISTRY; METALLURGY
    • C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10B—DESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B53/00—Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form
    • C10B53/07—Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form of solid raw materials consisting of synthetic polymeric materials, e.g. tyres
    • C—CHEMISTRY; METALLURGY
    • C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
    • C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
    • C10J3/02—Fixed-bed gasification of lump fuel
    • C10J3/20—Apparatus; Plants
    • C—CHEMISTRY; METALLURGY
    • C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
    • C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
    • C10J3/72—Other features
    • C10J3/80—Other features with arrangements for preheating the blast or the water vapour
    • F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/02—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
    • F23G5/027—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment pyrolising or gasifying stage
    • F23G5/0276—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment pyrolising or gasifying stage using direct heating
    • F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/44—Details; Accessories
    • F23G5/442—Waste feed arrangements
    • F23G5/448—Waste feed arrangements in which the waste is fed in containers or the like
    • C—CHEMISTRY; METALLURGY
    • C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10B—DESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B15/00—Other coke ovens
    • C10B15/02—Other coke ovens with floor heating
    • C—CHEMISTRY; METALLURGY
    • C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
    • C10J2300/00—Details of gasification processes
    • C10J2300/09—Details of the feed, e.g. feeding of spent catalyst, inert gas or halogens
    • C10J2300/0913—Carbonaceous raw material
    • C10J2300/0946—Waste, e.g. MSW, tires, glass, tar sand, peat, paper, lignite, oil shale
    • C—CHEMISTRY; METALLURGY
    • C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
    • C10J2300/00—Details of gasification processes
    • C10J2300/09—Details of the feed, e.g. feeding of spent catalyst, inert gas or halogens
    • C10J2300/0953—Gasifying agents
    • C10J2300/0956—Air or oxygen enriched air
    • C—CHEMISTRY; METALLURGY
    • C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
    • C10J2300/00—Details of gasification processes
    • C10J2300/09—Details of the feed, e.g. feeding of spent catalyst, inert gas or halogens
    • C10J2300/0953—Gasifying agents
    • C10J2300/0973—Water
    • C10J2300/0976—Water as steam
    • C—CHEMISTRY; METALLURGY
    • C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
    • C10J2300/00—Details of gasification processes
    • C10J2300/12—Heating the gasifier
    • C10J2300/1253—Heating the gasifier by injecting hot gas
    • C—CHEMISTRY; METALLURGY
    • C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
    • C10J2300/00—Details of gasification processes
    • C10J2300/16—Integration of gasification processes with another plant or parts within the plant
    • C10J2300/1603—Integration of gasification processes with another plant or parts within the plant with gas treatment
    • C10J2300/1606—Combustion processes
    • C—CHEMISTRY; METALLURGY
    • C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
    • C10J2300/00—Details of gasification processes
    • C10J2300/16—Integration of gasification processes with another plant or parts within the plant
    • C10J2300/1671—Integration of gasification processes with another plant or parts within the plant with the production of electricity
    • C—CHEMISTRY; METALLURGY
    • C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
    • C10J2300/00—Details of gasification processes
    • C10J2300/18—Details of the gasification process, e.g. loops, autothermal operation
    • C10J2300/183—Non-continuous or semi-continuous processes
    • F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2900/00—Special features of, or arrangements for incinerators
    • F23G2900/50005—Waste in combustion chamber supported on bed made of special materials
    • F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2900/00—Special features of, or arrangements for incinerators
    • F23G2900/54401—Feeding waste in containers, bags or barrels
    • Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E20/00—Combustion technologies with mitigation potential
    • Y02E20/12—Heat utilisation in combustion or incineration of waste

Definitions

  • the present disclosure relates to a process and equipment to process sorted and unsorted municipal solid waste [hereinafter "MSW”) to produce energy, typically in the forms of electricity or heat.
  • MSW Municipal solid waste
  • the system process allows for the maximum amount of energy to be retained, hydrocarbons to be driven from the MSW and syngas with an increased DTU value to be produced.
  • This disclosure provides processes, methods and equipment to enhance the 13TU value, or quality, of the syngas produced as well as significantly reduce the overall volume of waste, The waste can be reduced by up to 95% of its original volume while simultaneously reducing greenhouse gas emissions by up to 95%.
  • the present disclosure is directed to a reactor optimized for thermal
  • Thermal decomposition can process unsorted MSW and produce heat chat is used to operate boilers which in turn operate turbines to produce electricity
  • Gasification involves sorting the MSW, sizing (usually, grinding), drying and reforming the raw MSW into pellets prior to feeding into the gasification unit.
  • Pyrolysis involves sorting to remove unsuitable materials, then heating in the absence of oxygen resulting in the breakdown of the MSW into liquid hydrocarbons and syngas.
  • landfilling is currently the most popular method of disposing of waste. This method involves little capital investment to simply transport the waste to a suitable location to be dumped and covered. Additionally, municipal solid waste is currently one of the largest single producers of the greenhouse gas, methane, from countless landfills. The gas is generated from decomposing waste and it seeps into the atmosphere continually.
  • the present disclosure is directed to a method of processing MSW, either sorted or unsorted, which can be carried out through the use of canisters to hold the waste feedstock, and autoclaves specially designed to process the waste at suitable temperature and pressure combinations.
  • the final solid product is a mixture of carbon ash and noncombustible materials, such as, metals, drywall, etc., and syngas that has an enhanced BTU value, typically 300 to 700 BTU/ft 3 .
  • the remainder solid material generally amounts to approximately 5% of the original MSW volume. This material can then be sorted for metals with the balance being sent to a landfill or other recycling processes depending on its composition.
  • heat generated by the process can be recovered for useful applications.
  • the generated heat can transferred to, for instance, a hot oil system.
  • the hot oil system can circulate oil through two heat exchangers: one at the thermal processing chamber absorbing heat, and a second heat exchanger which can be an organic Rankine cycle, steam generator, water evaporator, or other heating system where the heat energy can be recovered, and used to generate steam to drive electricity producing turbines.
  • a canister or reactor for the thermal decomposition of waste material made up of a plurality of canister sections, a floor structure at the bottom of each one of the plurality of canister sections, a connector component located between any two of the canister sections, and a heated air opening for heated air introduction located in the floor structure in the lowest of the plurality of canister sections
  • the reactor can be composed of a single canister, instead of the stacked canisters as further described herein.
  • the presently disclosed method of thermally converting a solid waste feedstock into energy involves providing a solid waste feedstock; providing at least one holding canister; providing a sealable reactor vessel having a lower gas ignition chamber and configured to operate in both updraft and downdraft conditions; placing the solid waste feedstock into the holding canister; placing at least one holding canister into the sealable reactor vessel; sealing the sealable reactor vessel; purging the reactor vessel with air; engaging an oil/gas burner to begin the thermal decomposition process; providing heated air from the burner through an attached pipe into the lower portion of the reactor vessel and through to the lowest canister section until the canister section reaches a desired first temperature ranging from 500 to 1000 C; increasing temperature of the solid waste feedstock and pressure in the reactor vessel both to desired second temperature range, 400 to 1000 C, and second pressure levels, 4 to 150 psi, respectively; adjusting the pressure of the reactor vessel to a desired third pressure level, 20 to 100 psi, by adjusting the injection of compressed air; injecting water through atomizing
  • the present disclosure is also directed to a process for thermal decomposition of waste material by providing waste material, at least one of a plurality of canister sections having a central opening configured to accept heated air from a heater for holding the waste material, and a carbon pillow positioned between the heated air and the waste material, The plurality of canister sections are then placed in a sealable reaction vessel, where heated air is introduced through the central opening to thereby initiate the thermal decomposition of the waste material, the reaction conditions in the reaction vessel are maintained to thermal decompose the waste material, then the waste materials are quenched with water when the thermal decomposition is complete, and syngas is produced by the thermal decomposition of the waste material.
  • FIG. 1 is a plan drawing of the canister sections according to one embodiment of the present disclosure
  • FIG. 2 is a general schematic of an autoclave and gas handling device according to one embodiment of the present disclosure
  • Fig. 3 is a plan drawing of the autoclave and canisters according to one embodiment of the present disclosure.
  • Fig. 4 is a plan drawing of details of the canister sections according to one embodiment of the present disclosure.
  • batch processing of MSW either sorted or unsorted is carried out thru the use of canisters to hold the waste feedstock and specially designed autoclaves to process the waste at the desired temperature and pressure,
  • the canisters also function as an insulator to carry the majority of the heat from the process.
  • Syngas with an enhanced BTU value can be produced by the presently disclosed method.
  • the final solid product is a mixture of carbon ash and noncombustible materials (metals, drywall, etc.). This solid amounts to approximately 5% of the original volume.
  • the MSW can be received in either loose or baled.
  • the material can be placed inside cylindrical canisters which are then placed inside an autoclave to be thermally processed,
  • baled MSW is processed there is no need for the bales to be opened prior to being placed into a canister section, that is, the entire compressed bale can be placed into the canister section as received from the baler.
  • the canister 400 can be composed of one, two or three sections which can be stacked on top of one another to increase the amount of MSW processed in one autoclave run.
  • the sections can be attached to one another by a connecting ring(s) 420.
  • the canister can be a single unitary canister 470, which can be smaller, larger or the same size as the stacked canisters.
  • Each section of the canister can be loaded with either a bale of MSW or loose MSW, or in some cases, a mixture of the two, and then lifted into the autoclave and placed into position.
  • the canister sections can be stacked on top of each other in the autoclave.
  • the various waste feedstreams leading into the baler can include a variety of possible separated recycled or refuse components including food wastes, lawn and garden waste, plastics, rubber, liquid oil, grease, lubricants, or other hydrocarbon-containing liquids or gels.
  • metal pieces can be introduced into the material to be baled.
  • One reason for adding the metal pieces is to minimize dead zones inside the bale where material does not readily thermally decompose, This phenomenon is seen on an irregular basis during the presently disclosed process. While the exact mechanism of why decomposition does not occur has not been fully developed, it is currently understood that the introduction of void spaces can increase the efficiency of the decomposition process and decrease dead zones. The addition of the metal pieces can increase void spaces, also provide hot spots and increase conduction of thermal energy into more densely packed waste material.
  • the EPA broadly defines MSW as containing“everyday items such as product packaging, yard trimmings, furniture, clothing, bottles and cans, food, newspapers, appliances, electronics and batteries.”
  • Typical sources of MSW include residential, commercial, and institutional sites, although, the EPA's definition excludes industrial, hazardous, and construction and demolition waste, for the present disclosure such wastes can be included in the definition of MSW.
  • handling safeguards should be implemented to avoid undesirable side effects and contamination arising from the wastes,
  • the canister sections can be separated by a connecting ring located at the top of each section.
  • the upper section can be supported by Che connecting ring 170 to prevent the sections from further compressing the MSW located in the lower section.
  • the pins 140 pass through the hole in the connecting ring 170 and into the corresponding hole in the upper canister section.
  • the first or lowest section in the autoclave will be located directly above the gas heater chamber, As illustrated in Figs, 1A, IB and 1C, three of the canister sections can be stacked on top of each other to form a large unit 10.
  • the top of the gas heater chamber can be equipped with a solid metal plate or ring 450 to enable the thermal decomposition process to be started and maintained more easily.
  • a canister section can have a grate 410 or wire mesh 430 assembly at its end portion.
  • the grid properties can vary dependent on the properties of the MSW contained in the canister section, This
  • the heated air chamber located at the bottom of the autoclave can be equipped with a conical shaped heat deflector which can be composed of an appropriate metal to withstand the conditions, for instance, stainless steel.
  • the heat deflector 160 can be in a fluted cone shape as shown in Fig. 1 C and F.
  • the lowest canister section should be located above the highest part of the heat deflector to provide enough room from the bottom of the canister to the top of the heat deflector for the thermal conversion process to generate enough heat and air flow to allow for the creation of a thermal layer in the MSW present in the canisters.
  • the lower stage of the multi-stage canister can be equipped with a substantially dosed bottom 450 with a center opening for the heated air to be introduced there through.
  • the bottom of the lower stage canister can be equipped with a grating or perforated floor, 410, 430, to permit air flow.
  • the lower stage canister can have a conical structure 160 projecting up from tho circumference of the center opening.
  • a carbon pillow can be positioned around the conical structure to enhance the initial thermal decomposition process.
  • the carbon pillow can be composed primarily of charcoal.
  • the carbon pillow (not shown] can be positioned around and over the conical structure 160 and over the grated floor structure 430.
  • the carbon pillow can be thick enough that the heated air does not directly impact the solid waste material during the initial start-up operation of the thermal decomposition process.
  • the carbon pillow can be ton inches or more in depth.
  • the solid waste material is thermally converted to syngas during the presently disclosed thermal decomposition process, and does not come into direct contact with the heated air.
  • the upper stage of the multi-stage process canister reactor can have a perforated or grated floor or bottom structure (see 110, 130 and 150 of Fig. 1] that should be constructed so that the floor can support the bale of compressed MSW or other materials deposited therein to be thermally processed.
  • the bottom structure can include reinforcing bars or supports across the canister. Additionally, the bottom structure should be able to support any non-processed materials that remain after the thermal
  • decomposition process is stopped, and stop them from falling down into a lower stage canister section of the canister reactor.
  • the canister sections can be equipped with air vents 120 at appropriate locations to control the thermal reaction within the canister. These air vents can be set, in some instances, to a desired opening prior to the insertion of the filled canisters into the autoclave. In some embodiments of the canisters, the top 100 and the vents 120 can both independently of one another be present during the thermal decomposition process.
  • the cylindrical canister sections arc sized to accommodate a standard size bale of compressed MSW as illustrated in Fig. 5. These bales typically weigh from between 1000 to 2600 pounds.
  • the bales can be produced in various dimensions. Typically the bales are 3 to 5 feet high, but can be as tall as 12 feet high, the bale diameter can be about 4 to 5 feet.
  • the presently disclosed system is not limited to a certain size or dimension of the baled MSW but can be sized, larger or smaller, to accommodate the size of the available bales. Certain properties such as conversion efficiencies or increased BTU value of the gas may be impacted by the bale size.
  • the MSW can be baled without sorting of the waste, and in other embodiments the waste can be sorted on the basis of its BTU content.
  • high density BTU waste materials, plastics and rubber-containing items, like tires can be separated from lower density BTU waste material like newspaper, food or yard waste.
  • the separated items can be compressed into separate bales, or in some embodiments, the separated items can be re-mixed to obtain an MSW mixture with an average baseline BTU content in each bale.
  • liquid waste materials can also be added.
  • Liquid wastes such as used motor oils or lubricants can increase the BTU content of the baled material.
  • each canister section of the presently disclosed system allows for one or more of the canisters to be loaded with loose MSW while other canisters can be loaded with baled MSW, This flexibility allows for larger items to be processed without the need for baling, As mentioned above, the size of the grid or grate at the lower opening of the canister section can be quite large with bulk or large items, and substantially smaller with a bale of MSW.
  • FIG. 2 An overview of one embodiment of the present teachings is provided in Fig. 2, with the autoclave 210 containing the canisters 10 filled with MSW at the left hand side.
  • Air 200 for the thermal conversion of the MSW is added to the autoclave and the resulting enhanced BTU syngas 220 is produced.
  • the syngas can then be mixed, as necessary to sustain combustion, with a secondary fuel 240 such as diesel, natural gas or propane, and air 230, and then combusted in a burner assembly 2S0 to produce heated gas.
  • the heated gas can then be sent through a heat exchanger 260 to transfer its energy to an Organic Rankine Cycle ("ORC”) or steam boiler to produce electricity.
  • ORC Organic Rankine Cycle
  • the heated gas can then pass through an air cleaning assembly for subsequent release to the environment.
  • All components of the cylindrical canisters can be assembled of stainless steel or low carbon steel depending on the structural requirements of the environment.
  • the grates between the sections of the canisters can be composed of, for example, low carbon steel, while any wire mesh separating the sections or laying on top of a grate can be composed of stainless steel.
  • Temperatures and pressures during the thermal conversion process can be monitored by means of heat and pressure sensors located throughout the autoclave.
  • the sensors can be located at the top dome, the top, middle and bottom canister sections, the inner shield and the various process lines entering and leaving the autoclave.
  • the sensors can be installed using known methods through the walls of the autoclave to allow for measurements of reactor conditions during the thermal conversion process,
  • the autoclave according to the present disclosure can include means to operate in both updraft and downdraft conditions. Those means include ports or inlets/outlets for compressed air or another suitable fluid medium located at, at least, the top and bottom portions of the autoclave.
  • the autoclave provides for various inputs and outputs 342, 344, 352, 354, during the thermal conversion cycle with at least one compressed air inlet 200, 352, at least one atomized water inlet 342, quenching water 344, at least one counter flow control outlet 354, at least one inlet for heated air 360, and at least one outlet for the produced syngas 220, 360
  • the thermal shield 346 is attached to the autoclave by at least posts 340, ceramic coating 348 can be on the interior of the autoclave, and a heat reflective plate 350 is under the canister.
  • the inlets and outlets for the various components can be shared, that is, the component moving through a particular opening can be varied dependent on the stage of the process.
  • Additional features of the illustrated embodiment of the reaction vessel include changes from the reactor vessel described in U,S, Patent No. 8,713,582 Bl. Those changes include, but are not limited to, a smaller thermal shield surrounds the canister inside the autoclave so that at least portion of the top and bottom canister sections is located outside of the thermal shield, and an atomized water inlet,
  • One embodiment of the presently disclosed process involves placing a carbon pillow into the bottom of the lowest canister section to provide a layer between the ignition gas and the MSW, The carbon can be ignited by the heated air, and thereby turn into a thermal layer.
  • the MSW is not contacted directly with the heated air from the heater but rather the carbon pillow is ignited which in turn begins the thermal conversion of the MSW, During the downdraft cycle, the thermal layer will still continue upwards thru the MSW while the process gases will pass down thru the carbon layer. It is understood that as the gases pass through the carbon layer any aromatic cyclical hydrocarbon ring compounds present can bo broken down.
  • Unsorted MSW can be then loaded into a canister which in turn is placed into the autoclave,
  • the waste can be placed loosely into a canister or compressed bales maybe placed into the canisters.
  • the bales are cylindrical and sized to fit in the canisters of the present teachings.
  • the bales can be compressed between 100 and 1000 psi.
  • the conversion process according to the present disclosure is a combination of updraft and downdraft gasification in a low oxygen atmosphere at pressure.
  • the process begins in a startup cycle which involves opening the counter flow valve, then opening the ignition gas valve and an air inlet valve. This process produces a Venturi effect that draws a vacuum/negative pressure on the counter flow line,
  • a burner which can be supplied with one or more of natural gas, propane or diesel provides the thermal energy to start the thermal conversion of the carbon pillow.
  • the burner is located on the process line and produces heated air that travels into the bottom of the autoclave to ignite the carbon pillow.
  • the gas/diesel burner is then engaged until a temperature sensor on the counter flow line reaches the desired temperature, typically between 250 to 1000 C. In some cases, the burner operates for 5 to 10 minutes, in other cases, this process can last up to 25 minutes and appears to be dependent on feedstock variations.
  • the process produces a carbon dioxide rich atmosphere which provides the necessary elements for a reverse Boudouard Reaction.
  • the startup cycle is complete when the burner is turned off, and the burner valve, Venturi, and the counterfiow valves are all closed.
  • the next step in the process is the updraft process which begins with the opening, at about 5 to 20% open, of a process valve and the main compressed air valve is also opened at about 2 to 20% open.
  • the updraft process begins to build in both pressure, to about 4 to 6 bar (60 to 100 psi), and temperature, to about 100 to 1000 C, as measured on tho process thermocouple located on the process line leaving the autoclave.
  • Atomized water can be injected into the autoclave during the process to control the temperature at the Hue gas exit thermocouple to between about 500 to 1000 C.
  • the water is also understood to initiate a water gas shift reaction which enhances the BTU valuo of the syn gas produced, Water can be injected from the top of the autoclave and also from side ports to contain the thermal conversion at lower sections of the autoclave.
  • the updraft step continues maintaining a temperature of 100 to 700 C measured at the process line thermocouple that is located on the process line leaving the autoclave,
  • the process is then converted to downdraft to complete the thermal breakdown of all the material in the MSW into simple gases.
  • the MSW material generates mainly C1 thru C4 gases.
  • the downdraft operation provides the added benefit of forcing the off gas thru the thermal layer which can break down any larger molecules present in the gas, such as aromatic hydrocarbon rings.
  • the presently disclosed process can be continued until a desired endpoint is reached.
  • the desired endpoint may be, but is not limited to, the point at which the MSW feedstock is ij converted to ash, black carbon, char or charcoal, or ii] reduced in mass to a level equal to approximately 10% or less of the original MSW feedstock mass,
  • the MSW feedstock can then be quenched with steam, The remaining heat from the MSW feedstock superheats the steam to drive hydrocarbons off and produce hydrogen.
  • the holding canister is then removed from the reactor vessel and the remaining ash, minerals, glass, gypsum, carbon and non-combustibles can be removed from the holding canister.
  • the syngas produced from the thermal conversion of the MSW is then piped to a separate combustion chamber 250 located outside of the autoclave 210.
  • the syngas is mixed with air and combusted to produce more heat energy.
  • the combustion chamber can be equipped with a continuously lit pilot burner fueled with any one of natural gas, propane and/or diesel.
  • the second burner 240 acts as a pilot as well as a backup heater to allow the combustion chamber to continue to develop heat.
  • Fig. 2 One possible embodiment of this syngas combustion system is illustrated in Fig. 2,
  • the heat from the combustion of the syngas is transferred thru a heat exchanger 260 to a suitable fluid medium 270, 280, such as synthetic oil or water.
  • a suitable fluid medium such as synthetic oil or water.
  • the fluid medium can then be circulated thru a heat engine (not shown], such as an ORC engine to produce electricity
  • the final emissions can be mixed with fresh air, optionally sent through a wet scrubber 262 to reduce the temperature, then further cooled by a blower 266 with a fresh air intake 268, passed through an air filtering system 272, such as a Blue Sky Filtering system, then through a HEPA filter 290,
  • an air filtering system 272 such as a Blue Sky Filtering system
  • the presently disclosed process can reduce the greenhouse gas foot print of the MSW by 95%.
  • the presently disclosed process for the conversion of MSW feedstock to less than 5% of its original volume can have reversible process flows, allowing gases to flow both upward and downward.
  • the thermal conversion of the MSW feedstock can be in both downdraft and updraft directions.
  • a reactor for the thermal decomposition of waste material is also taught by the present disclosure.
  • the reactor can include a plurality of canister sections, a floor structure at the bottom of each one of the plurality of canister sections, a connector component located between any two of the canister sections, and a heated air opening for heated air introduction located in the floor structure in the lowest of the plurality of canister sections.
  • the present reactor can be placed into an autoclave suitable of holding the plurality of canister sections. In most instances, there are at most three canister sections in the autoclave during one thermal decomposition run; although the size of the autoclave and the canister sections will obviously impact the number of canister sections present.
  • the bottom most canister section can include a conical structure centrally positioned above the heated air opening with a carbon pillow positioned around the conical structure configured to prevent the heated air from directly contacting the waste material.
  • the carbon pillow can be, in some embodiments of the presently disclosed system, ten inches or more thick.
  • One purpose of the carbon pillow is to prevent direct impact of the heated air on the compressed or loose MSW.
  • the reactor can have a floor structure comprising a grated structural component configured to allow for airflow and support for the waste material.
  • a grated structural component configured to allow for airflow and support for the waste material.
  • the floor structure can be a solid plate having a central heated air opening, and in some cases, a grated structural component can be located above the solid plate and its central heated air opening.
  • At least one of the canister sections can include openings for venting of process gas, or introduction of additional reaction components.
  • the disclosed process for thermal decomposition of waste material first involves providing waste material, and at least one of a plurality of canister sections having a central opening configured to accept heated air from a heater for holding the waste material, and a carbon pillow as described above.
  • a single canister section can be utilized in place of the stacked plurality of canister sections.
  • the next step is to place the plurality of canister sections in a sealable reaction vessel, and introducing a heated air through the central opening to thereby initiate the thermal decomposition of the waste material.
  • the reaction conditions in the reaction vessel need to be maintained to thermal decompose the waste material.
  • the waste materials can be quenched with water, and the syngas is produced by the thermal decomposition of the waste material can be collected.
  • Thermal decomposition occurs with reaction conditions comprise temperatures ranging from 400 to 850 C, and vessel pressures ranging from 4 to 200 psi. Those conditions are maintained after the heated air is extinguished, and the thermal conversion of the waste material is initiated. [0066] With the tightly compressed bales at times, dead zones where the thermal decomposition is limited, are present. By adding metal pieces to the waste material, the dead zones are diminished in places where the metal pieces are added in an amount sufficient to red uce the amount of non-thermally decomposed waste material.
  • the waste material can be provided as a cylindrical bale of compressed waste material wrapped with a protective material to maintain the waste material in a compressed condition.
  • the waste material can be provided as loose waste material. It is also possible to have one canister section with a compressed bale and another canister section with loose material, or even a mix of the two forms in one canister section,
  • a sealable reactor vessel generally suitable for used with the presently disclosed method can include the apparatus generally described in the applicant’s prior patent, U.S. Patent No. 8,715,502 B2, the disclosure of which is incorporated by reference herein in its entirety for all purposes.

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Organic Chemistry (AREA)
  • Combustion & Propulsion (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Environmental & Geological Engineering (AREA)
  • Processing Of Solid Wastes (AREA)
  • Coke Industry (AREA)

Abstract

La présente invention concerne un système de réacteur constitué d'une seule cartouche ou d'une pluralité de sections de cartouche séparées pour le traitement de conversion chimique thermique avancé de déchets solides municipaux ("MSW"), soit triés, soit non triés, et d'autoclaves spécialement conçus pour traiter les déchets à des combinaisons de température et de pression appropriées. Les sections de cartouche peuvent être remplies individuellement et séparément avec des balles compressées de MSW ou avec des MSW en vrac sélectionnés. La présente invention concerne également un procédé de traitement MSW, triés ou non triés, qui peut être mis en œuvre par le biais de l'utilisation de cartouches pour contenir la charge d'alimentation de déchets, et d'autoclaves spécialement conçus pour traiter les déchets à des combinaisons de température et de pression appropriées. Le système de réacteur peut produire un gaz de synthèse qui présente une valeur BTU améliorée, typiquement entre environ 300 et 700 BTU/ft3. Le matériau de déchets solides restant s'élève généralement à environ 5 % du volume d'origine de MSW. Ce matériau peut ensuite être trié à la recherche de métaux, le reste étant envoyé à une décharge ou à d'autres processus de recyclage en fonction de sa composition.
EP20759916.8A 2019-02-20 2020-02-20 Procédé et système pour la décomposition thermique de déchets solides municipaux Active EP3928031B1 (fr)

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US201962807798P 2019-02-20 2019-02-20
PCT/CA2020/000017 WO2020168411A1 (fr) 2019-02-20 2020-02-20 Procédé et réacteur pour le traitement de conversion chimique thermique avancé de déchets solides municipaux

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JP (1) JP2022521270A (fr)
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AU (1) AU2020225085A1 (fr)
BR (1) BR122021017230A2 (fr)
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US20200263100A1 (en) 2020-08-20
CN113631860A (zh) 2021-11-09
AU2020225085A1 (en) 2021-10-07
EP3928031B1 (fr) 2024-04-03
US11098251B2 (en) 2021-08-24
EP3928031A4 (fr) 2022-11-23
US11584893B2 (en) 2023-02-21
BR112021016561A2 (pt) 2021-11-03
BR122021017230A2 (pt) 2021-11-16
CA3130625A1 (fr) 2020-08-27
JP2022521270A (ja) 2022-04-06
US20200263093A1 (en) 2020-08-20
MX2021010079A (es) 2023-02-17
CA3130625C (fr) 2022-05-03
WO2020168411A1 (fr) 2020-08-27

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